The University of Queensland, Advanced Water Management Centre, Queensland, 4072, Australia.
The University of Queensland, Advanced Water Management Centre, Queensland, 4072, Australia; ICRA, Catalan Institute for Water Research, Scientific and Technological Park of the University of Girona, H(2)O Building, Emili Grahit 101, 17003, Girona, Spain; ICREA, Catalan Institute for Research and Advanced Studies, 08010, Barcelona, Spain.
Water Res. 2016 Dec 1;106:550-561. doi: 10.1016/j.watres.2016.10.022. Epub 2016 Oct 8.
Ozonation is known to generate biodegradable organic matter, which is typically reduced by biological filtration to avoid bacterial regrowth in distribution systems. Post-chlorination generates halogenated disinfection byproducts (DBPs) but little is known about the biodegradability of their precursors. This study determined the effect of ozonation and biofiltration conditions, specifically ozone exposure and empty bed contact time (EBCT), on the control of DBP formation potentials in drinking water. Ozone exposure was varied through addition of HO during ozonation at 1 mgO/mgDOC followed by biological filtration using either activated carbon (BAC) or anthracite. Ozonation led to a 10% decrease in dissolved organic carbon (DOC), without further improvement from HO addition. Raising HO concentrations from 0 to 2 mmol/mmolO resulted in increased DBP formation potentials during post-chlorination of the ozonated water (target Cl residual after 24 h = 1-2 mg/L) as follows: 4 trihalomethanes (THM4, 37%), 8 haloacetic acids (HAA8, 44%), chloral hydrate (CH, 107%), 2 haloketones (HK2, 97%), 4 haloacetonitriles (HAN4, 33%), trichloroacetamide (TCAM, 43%), and adsorbable organic halogen (AOX, 27%), but a decrease in the concentrations of 2 trihalonitromethanes (THNM2, 43%). Coupling ozonation with biofiltration prior to chlorination effectively lowered the formation potentials of all DBPs including CH, HK2, and THNM2, all of which increased after ozonation. The dynamics of DBP formation potentials during BAC filtration at different EBCTs followed first-order reaction kinetics. Minimum steady-state concentrations were attained at an EBCT of about 10-20 min, depending on the DBP species. The rate of reduction in DBP formation potentials varied among individual species before reaching their minimum concentrations. CH, HK2, and THNM2 had the highest rate constants of between 0.5 and 0.6 min followed by HAN4 (0.4 min), THM4 (0.3 min), HAA8 (0.2 min), and AOX (0.1 min). At an EBCT of 15 min, the reduction in formation potential for most DBPs was less than 50% but was higher than 70% for CH, HK2, and THNM2. The formation of bromine-containing DBPs increased with increasing EBCT, most likely due to an increase in Br/DOC ratio. Overall, this study demonstrated that the combination of ozonation and biofiltration is an effective approach to mitigate DBP formation during drinking water treatment.
臭氧氧化已知会生成可生物降解的有机物,这些有机物通常通过生物过滤来减少,以避免在配水系统中细菌的再生。后氯化会生成卤代消毒副产物(DBP),但对于其前体的可生物降解性知之甚少。本研究确定了臭氧氧化和生物过滤条件(特别是臭氧暴露和空床接触时间(EBCT))对饮用水中 DBP 形成潜力控制的影响。臭氧暴露通过在 1 mgO/mgDOC 下进行臭氧氧化时添加 HO 来改变,然后使用活性炭(BAC)或无烟煤进行生物过滤。臭氧氧化导致溶解有机碳(DOC)降低 10%,但添加 HO 没有进一步改善。随着 HO 浓度从 0 增加到 2 mmol/mmolO,在对臭氧氧化水进行后氯化时,DBP 形成潜力增加(24 小时后的目标 Cl 残留量为 1-2 mg/L),如下所示:4 种三卤甲烷(THM4,37%)、8 种卤代乙酸(HAA8,44%)、氯仿(CH,107%)、2 种卤代酮(HK2,97%)、4 种卤代乙腈(HAN4,33%)、三氯乙酰胺(TCAM,43%)和可吸附有机卤素(AOX,27%),但 2 种三卤硝基甲烷(THNM2,43%)的浓度降低。在氯化之前,将臭氧氧化与生物过滤相结合,可有效降低所有 DBP 的形成潜力,包括 CH、HK2 和 THNM2,这些物质在臭氧氧化后均增加。在不同 EBCT 下通过 BAC 过滤时,DBP 形成潜力的动力学遵循一级反应动力学。在大约 10-20 分钟的 EBCT 下达到最小稳态浓度,具体取决于 DBP 种类。在达到最小浓度之前,个别物质的 DBP 形成潜力的减少速率有所不同。CH、HK2 和 THNM2 的速率常数在 0.5 到 0.6 分钟之间,其次是 HAN4(0.4 分钟)、THM4(0.3 分钟)、HAA8(0.2 分钟)和 AOX(0.1 分钟)。在 EBCT 为 15 分钟时,大多数 DBP 的形成潜力降低不到 50%,但 CH、HK2 和 THNM2 的降低超过 70%。随着 EBCT 的增加,含溴 DBP 的形成增加,这很可能是由于 Br/DOC 比值的增加。总的来说,本研究表明,臭氧氧化和生物过滤的组合是一种有效控制饮用水处理过程中 DBP 形成的方法。